4.7 Article

Degradation of organic pollutants in near -neutral pH solution by Fe-C micro-electrolysis system

Journal

CHEMICAL ENGINEERING JOURNAL
Volume 315, Issue -, Pages 403-414

Publisher

ELSEVIER SCIENCE SA
DOI: 10.1016/j.cej.2017.01.042

Keywords

Fe-C micro-electrolysis; Degradation pathway; Organic pollutants; Near-neutral pH; Mechanism

Funding

  1. National Natural Science Foundation of China [21276012, 21576010, U1607107]
  2. Fundamental Research Funds for the Central Universities [BUCTRC201515]
  3. Higher Education and High-quality and World-class Universities [PY201607]
  4. BUCT Fund for Disciplines Construction and Development [XK1508]

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The degradation of organic pollutants in the simulated and realistic wastewaters was investigated by Fe C micro-electrolysis system. Effects of initial pH, Fe/C mass ratio, gas bubbling type (air or N-2) and the type of anions on degradation and mineralization of Sunset Yellow (SY) were studied. The degradation and mineralization efficiencies of 500 mg L-1 SY were approximately 99.0% and 77.5% after 90 min treatment, when the initial pH, Fe/C ratio and air bubbling flow rate were 6.0, 1:1 and 45 Lh(-1), respectively. Besides, the type of anions had a significant influence on the Fe-C micro-electrolysis process. The results of kinetics study indicated that Fe-C micro-electrolysis process followed second-order-kinetics well. The degradation pathway and mechanism for SY were proposed based on FTIR and LC-MS analyses of treated wastewater. Additionally, the Fe-C micro-electrolysis process could dispose linear alkyl chain and benzene ring compounds efficiently under the optimal conditions, and the mineralization efficiencies Were in the range of 94-96% and approximately 80%, respectively. The degradation feasibility of a realistic wastewater by the Fe-C micro-electrolysis system was investigated with landfill leachate. In conclusion, Fe-C micro-electrolysis system is an effective and promising technology for organic wastewater treatment in near-neutral pH condition. (C) 2017 Elsevier B.V. All rights reserved.

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